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Scotland's Wildlife – an assessment of biodiversity in 20

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9 Upl<strong>an</strong>d ecosystems<br />

The extent <strong>an</strong>d stature <strong>of</strong> Scotl<strong>an</strong>d’s upl<strong>an</strong>ds are dist<strong>in</strong>ctive, both <strong>in</strong> terms <strong>of</strong> the rugged<br />

l<strong>an</strong>dscape character <strong>an</strong>d r<strong>an</strong>ge <strong>of</strong> habitats not duplicated elsewhere <strong>in</strong> the world.<br />

Accord<strong>in</strong>g to the Countryside Survey report for Scotl<strong>an</strong>d, published <strong>in</strong> <strong>20</strong>09, over half <strong>of</strong><br />

Scotl<strong>an</strong>d’s l<strong>an</strong>d area (55%) is upl<strong>an</strong>d habitat: mont<strong>an</strong>e (0.5%); <strong>in</strong>l<strong>an</strong>d rock (1%);<br />

bracken (1.6%); fen, marsh & swamp (3%); dwarf shrub heath (11%); acid grassl<strong>an</strong>d<br />

(12%); <strong>an</strong>d bog (26%). Mont<strong>an</strong>e <strong>an</strong>d <strong>in</strong>l<strong>an</strong>d rock are <strong>in</strong>sufficiently represented <strong>in</strong> the<br />

sample to be reported on. The five that are sufficiently represented, <strong>in</strong> order <strong>of</strong><br />

magnitude, are described here.<br />

9.1 Habitat extent<br />

Bracken<br />

Although the bracken pl<strong>an</strong>t is natural <strong>in</strong> Scotl<strong>an</strong>d, <strong>in</strong>festation c<strong>an</strong> degrade habitats like<br />

heather moorl<strong>an</strong>d <strong>an</strong>d, be<strong>in</strong>g unpalatable, disproportionately reduce the productivity <strong>of</strong><br />

hill graz<strong>in</strong>g as it rapidly colonises deeper soils on the most fertile ground. Where<br />

scattered <strong>in</strong> relatively small patches, bracken is difficult to detect <strong>an</strong>d measure <strong>in</strong><br />

sample surveys. Countryside Survey reports only on dense st<strong>an</strong>ds, where bracken<br />

exceeds 95% cover. The extent <strong>of</strong> bracken rema<strong>in</strong>ed essentially unch<strong>an</strong>ged between<br />

1998 <strong>an</strong>d <strong>20</strong>07 (<strong>an</strong> apparent <strong>in</strong>crease <strong>of</strong> 8%, from 121,000ha to 131,000ha, was not<br />

statistically signific<strong>an</strong>t). The <strong>in</strong>terch<strong>an</strong>ge <strong>of</strong> ga<strong>in</strong>s <strong>an</strong>d losses between habitats is<br />

illustrated <strong>in</strong> Figure 9.1.<br />

Bracken <strong>in</strong>creased signific<strong>an</strong>tly <strong>in</strong> the <strong>in</strong>termediate upl<strong>an</strong>ds <strong>an</strong>d isl<strong>an</strong>ds, where it was<br />

already most abund<strong>an</strong>t, from 49,000ha <strong>in</strong> 1998 to 62,000ha <strong>in</strong> <strong>20</strong>07.<br />

Figure 9.1<br />

Ch<strong>an</strong>ge <strong>in</strong> the extent <strong>of</strong> bracken broad habitat between 1998 <strong>an</strong>d <strong>20</strong>07<br />

Source: Countryside Survey <strong>20</strong>07<br />

Note: negative ch<strong>an</strong>ges (losses) are scaled differently from positive ch<strong>an</strong>ges (ga<strong>in</strong>s)<br />

losses<br />

80% unch<strong>an</strong>ged<br />

ga<strong>in</strong>s<br />

5% heath<br />

6% acid grassl<strong>an</strong>d<br />

9% other<br />

1<strong>20</strong>000<br />

100000<br />

80000<br />

60000<br />

40000<br />

<strong>20</strong>000<br />

0<br />

-<strong>20</strong>000<br />

area (ha)<br />

58

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